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Method for separating polybrominated diphenylether from waste electronic plastic

A polybrominated diphenyl ether and plastic technology, applied in plastic recycling, bulk chemical production, recycling technology and other directions, can solve the problems of long time for dissolution, extraction and separation, affecting the safe use of resin, increasing regeneration cost, etc., and avoiding solvent Distillation regeneration process, avoid low extraction efficiency, reduce the effect of separation load

Inactive Publication Date: 2012-01-11
MAOMING COLLEGE
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  • Summary
  • Abstract
  • Description
  • Claims
  • Application Information

AI Technical Summary

Problems solved by technology

However, there are the following problems in adopting this patent method to reclaim polybrominated diphenyl ether flame-retardant plastics: (1) decabromodiphenyl ether still has a solubility of 0.1 to 0.2wt% in these solvents at room temperature, and polybrominated diphenyl ethers below nonabromine The solubility of phenyl ether is larger. Due to the high boiling point and low volatility, most of the dissolved polybrominated diphenyl ethers cannot be removed with the solvent in the subsequent vacuum evaporation process, and the polybrominated diphenyl ethers in the regenerated resin thus obtained The concentration will still be higher than the ROHS standard
(2) In the stage of vacuum evaporation to remove solvent, as the concentration of solvent decreases, the viscosity of the system increases sharply, and the residual rate of solvent in the final recycled plastic is too high. If the selected solvent is toxic solvents such as toluene, tetrahydrofuran, and chloroform , too much residue will affect the safe use of the resin
If a natural low-toxic solvent such as limonene is used, the solvent residue problem will not affect the application of recycled plastic products, but due to the high price of such solvents, excessive solvent residue will greatly increase the recycling cost
[0008] It can be seen that the above-mentioned method for separating polybrominated diphenyl ethers from flame retardant plastics generally has one or more of the following deficiencies: (1) the residual solvent is too large, which affects the use and separation cost of the resin; (2) the cost of recycled resin products Although polybrominated diphenyl ether has been reduced, it still cannot meet the requirements of the RoHS directive; (3) due to the high viscosity of plastics and low mass transfer rate, the dissolution, extraction and separation time is long and the efficiency is low. (4) decabromodiphenyl ether in plastics The concentration of phenylene ether is high, and the solubility in general organic solvents and supercritical solvents is small, resulting in low separation efficiency and poor separation effect (5) Liquid-solid extraction separation of flame retardants in plastics is affected by the size of the contact interface, and the separation speed is slow
Due to the above deficiencies in the current technology, it cannot fully satisfy the regeneration of PBDE flame-retardant waste electronic and electrical plastics.

Method used

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Examples

Experimental program
Comparison scheme
Effect test

example 1

[0040] Add 1 kg of broken plastic particles (mainly HIPS) and 4 kg of toluene containing 8% decabromodiphenyl ether into a 10-liter dissolving kettle, stir and dissolve at room temperature for 50 min, and pass the solution through a coarse filter (filtering net) The hole diameter is 0.5mm), and 4.9kg of polymer solution and about 0.1kg of insoluble plastic particles and impurities such as screws, glass, and sand are obtained. The polymer solution was filtered through a centrifugal filter to separate 0.14kg of sludge-like residue and 4.74kg of residue at a speed of 13,000 rpm. Sampling analysis found that the residue was mainly composed of decabromodiphenyl ether, di Antimony, calcium carbonate, carbon black and other components are composed of particles. The concentration of decabromodiphenyl ether in the filter solution is 0.19%. Take 1kg filter solution and pour it into a 10-liter supercritical extraction kettle, and feed 4kg at a temperature of 40 ℃, supercritical CO at a p...

example 2

[0042] Add 1 kg of broken plastic particles (mainly HIPS) and 4 kg of d-limonene containing 10% decabromodiphenyl ether into a 10-liter dissolving kettle, stir and dissolve at 60°C for 50 minutes, and put the solution into a coarse filter 4.85kg of polymer solution and about 0.15kg of insoluble plastic sheets and impurities such as screws, glass, and gravel were obtained. Filter the polymer solution through a centrifugal filter to separate 0.13kg of sludge-like slag and 4.75kg of slag. Sampling analysis found that the slag was mainly composed of decabromodiphenyl ether, antimony trioxide, calcium carbonate, carbon black, etc. The particle composition of the components, the concentration of decabromodiphenyl ether in the filter solution is 0.2%, take 1kg filter solution and pour it into a 10 liter supercritical extraction kettle, and pass into 4kg of supercritical extraction tank whose temperature is 60 ℃ and pressure is 13MPa. CO 2 Contact extraction for 20min, the polymer is...

example 3

[0044] Add 1kg of waste TV casing broken plastic particles (mainly HIPS) and 4kg of d-limonene containing 8% decabromodiphenyl ether and 2% octabromodiphenyl ether to a 10-liter dissolving kettle and stir at 60°C Dissolve for 50 minutes, put the solution into a coarse filter (with a mesh size of 0.5 mm), and obtain 4.85 kg of polymer solution and about 0.15 kg of insoluble plastic sheets and impurities such as screws, glass, and gravel. Filter the polymer solution through a centrifugal filter to separate 0.13kg of sludge-like slag and 4.75kg of slag. Sampling analysis found that the slag was mainly composed of decabromodiphenyl ether, antimony trioxide, calcium carbonate, carbon black, etc. Particle composition of components, the concentration of decabromodiphenyl ether in the filter solution is 0.18%, get 1kg filter solution and pour into a 10 liter supercritical extraction kettle, and pass into 4kg temperature is 60 ℃, the pressure is 10.5MPa super Critical CO 2 Contact ext...

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Abstract

The invention provides a method for separating polybrominated diphenylether from waste electronic plastic, comprising the following steps of: dissolving waste electronic plastic with an organic solvent to form a polymer solution; then refining the polymer solution through rough filtration and centrifugal filtration in sequence; contacting the filtered polymer solution with supercritical CO2 for extracting to reduce the solubility of polymer; precipitating the dissolved polymer in a solid state form; and separating out liquid phase and realizing the separation of the polymer and the polybrominated diphenylether. By adopting the separated polybrominated diphenylether from the waste electronic plastic, not only the concentration of polybrominated diphenylether in regenerated plastic can meetthe requirement on RoHS (Restriction of Hazardous Substance) instruction, but also solvent residue in the regenerated plastic can be reduced to safety level. In addition, by adopting the invention, the purity of regenerated plastic products can be improved, and favorable mechanical property is reserved, thereby realizing the high-efficiency and safe recycling of the waste electronic plastic.

Description

technical field [0001] The invention relates to the technical field of utilization of waste electronic plastics, in particular to a method for separating polybrominated diphenyl ethers from waste electronic plastics, which is suitable for recycling flame-retardant waste electronic plastics. Background technique [0002] The dismantling and recycling process of waste electronic and electrical equipment produces a large amount of plastic waste. Due to safety and fire prevention, these plastics are generally added with 5-20% brominated flame retardants, decabromodiphenyl ether, octabromodiphenyl ether is the main type. Polybrominated diphenyl ethers have been proven to be a class of persistent organic pollutants harmful to the environment, biology and human health. Therefore, the European Union issued the "Restriction on the Use of Certain Hazardous Components in Electrical and Electronic Equipment" (RoHS Directive) It clearly stipulates that since July 1, 2006, the mass fract...

Claims

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Application Information

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Patent Type & Authority Patents(China)
IPC IPC(8): C08J11/08B01D11/04
CPCY02P20/54Y02W30/62
Inventor 彭绍洪陈烈强胡亚林
Owner MAOMING COLLEGE
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